JP2001054775A - Method and device for reducing lead and chlorine - Google Patents

Method and device for reducing lead and chlorine

Info

Publication number
JP2001054775A
JP2001054775A JP11233885A JP23388599A JP2001054775A JP 2001054775 A JP2001054775 A JP 2001054775A JP 11233885 A JP11233885 A JP 11233885A JP 23388599 A JP23388599 A JP 23388599A JP 2001054775 A JP2001054775 A JP 2001054775A
Authority
JP
Japan
Prior art keywords
chlorine
lead
alkali
amount
clinker
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP11233885A
Other languages
Japanese (ja)
Other versions
JP4283947B2 (en
Inventor
Yasushi Yamamoto
泰史 山本
Tetsuo Ogiri
哲雄 大桐
Yoshihisa Tanaka
宣久 田中
Koichiro Sato
宏一郎 佐藤
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Taiheiyo Cement Corp
Original Assignee
Taiheiyo Cement Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Taiheiyo Cement Corp filed Critical Taiheiyo Cement Corp
Priority to JP23388599A priority Critical patent/JP4283947B2/en
Publication of JP2001054775A publication Critical patent/JP2001054775A/en
Application granted granted Critical
Publication of JP4283947B2 publication Critical patent/JP4283947B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/10Production of cement, e.g. improving or optimising the production methods; Cement grinding

Landscapes

  • Curing Cements, Concrete, And Artificial Stone (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide the method and device for reducing both of lead and chlorine in a clinker. SOLUTION: In the method, a lead compd. is heated to a temp. above the boiling temp. of lead chloride under the presence of chlorine to convert the lead compd. to the lead chloride and to evaporate and remove the lead chloride. In this case, the lead compd. is evaporated and removed by adjusting chlorine quantity in excessive quantity than chemical equivalence based on lead content, moreover, residual chlorine is removed by converting the chlorine to alkali chloride by introducing alkali.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、塩素を利用して鉛
や鉛化合物(両者を含めて鉛化合物と云う)を除去する場
合に、鉛化合物の除去効果が高く、かつ残留塩素量が少
ない鉛・塩素の低減方法に関する。本方法は廃棄物から
鉛および塩素を除去して再利用する場合などに広く適用
することができる。特に、生活・産業廃棄物の焼却灰等
をセメント原料として利用する技術分野において有用で
ある。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for removing lead and a lead compound (both of which are referred to as a lead compound) by utilizing chlorine, the effect of removing the lead compound is high, and the residual chlorine amount is small. It relates to a method for reducing lead and chlorine. This method can be widely applied to the case where lead and chlorine are removed from waste and reused. In particular, it is useful in the technical field of using incinerated ash of domestic and industrial waste as a cement raw material.

【0002】[0002]

【従来技術】廃棄物に含まれる鉛化合物を除去する手段
として、塩素の存在下で焼成することにより鉛化合物を
塩化鉛に転じ、揮発除去する方法が従来から知られてい
る。このとき、鉛化合物と共にアルカリ金属が存在する
と、アルカリ金属は鉛よりも塩素と結合し易いので、鉛
化合物がアルカリ金属の影響を受け、その一部が酸化鉛
に転じて鉛の揮発が抑制され、鉛の残留量が多くなる。
これを解消するために塩素量を増すと、鉛化合物の残留
量は低減するが、今度は塩素の残留量が多くなると云う
問題がある。また、焼成温度を上げることによってクリ
ンカー中の酸化鉛を揮発させる方法もあるが、焼成温度
を酸化鉛が揮発する1350℃〜1400℃以上まで加
熱する必要があり、クリンカーが軟化してキルン内の煉
瓦壁面に付着したり、熱量が増加するため好ましくな
い。
2. Description of the Related Art As a means for removing lead compounds contained in wastes, there has been conventionally known a method of baking in the presence of chlorine to convert the lead compounds into lead chloride and volatilize them. At this time, if an alkali metal is present together with the lead compound, the alkali metal is more easily bonded to chlorine than lead, so that the lead compound is affected by the alkali metal, part of which is converted to lead oxide and the volatilization of lead is suppressed. , Lead content increases.
If the amount of chlorine is increased to solve this problem, the residual amount of the lead compound is reduced, but there is a problem that the residual amount of chlorine is increased this time. There is also a method of evaporating the lead oxide in the clinker by raising the firing temperature. However, it is necessary to heat the firing temperature to 1350 ° C. to 1400 ° C. or higher at which the lead oxide evaporates, and the clinker softens and the It is not preferable because it adheres to the brick wall surface and the amount of heat increases.

【0003】[0003]

【発明が解決しようとする課題】本発明は、塩素を利用
した鉛の除去方法における従来の上記問題を解決したも
のであり、鉛化合物に対する塩素量を調整すると共にア
ルカリ導入のタイミングを調整することにより、クリン
カ中のアルカリ量が0.75wt%を超えない範囲で、ク
リンカ中の塩素量を1000ppm以下、好ましくは、数
十ppmの水準に低減し、かつクリンカ中の鉛含有量を環
境基準に適合する60ppm以下とする方法を提供するも
のである。
SUMMARY OF THE INVENTION The present invention has been made to solve the above-mentioned conventional problems in a method for removing lead using chlorine, and it is an object of the present invention to adjust the amount of chlorine relative to a lead compound and the timing of introducing alkali. As a result, the chlorine content in the clinker is reduced to 1000 ppm or less, preferably several tens of ppm, and the lead content in the clinker is reduced to environmental standards within a range in which the alkali content in the clinker does not exceed 0.75 wt%. It is intended to provide a method for reducing the content to 60 ppm or less.

【0004】[0004]

【課題を解決する手段】すなわち本発明は、鉛化合物を
含有する材料を、塩素の存在下で塩化鉛の沸点以上に加
熱し、鉛化合物を塩化鉛に転じて揮発除去する方法にお
いて、塩素量を鉛含有量に対して化学当量より過剰量に
調整して鉛化合物を揮発除去し、さらにアルカリを導入
して残留する塩素をアルカリ塩化物に転じて加熱除去す
ることを特徴とする鉛・塩素の低減方法に関する。
That is, the present invention provides a method of heating a material containing a lead compound to a temperature higher than the boiling point of lead chloride in the presence of chlorine, converting the lead compound into lead chloride, and volatilizing and removing the amount of chlorine. Lead / chlorine characterized by adjusting the amount to be more than the chemical equivalent to the lead content to volatilize and remove the lead compound, further introducing an alkali to convert the remaining chlorine into an alkali chloride and removing by heating. To a method for reducing the amount of odor.

【0005】上記方法は、好ましくは、塩素量を鉛化合
物とアルカリの合計量に対する化学当量より過剰量に調
整して鉛化合物を揮発除去し、さらにアルカリを導入し
て残留する塩素を除去する鉛・塩素の低減方法である。
In the above method, preferably, the amount of chlorine is adjusted to an excess of a chemical equivalent to the total amount of the lead compound and the alkali to volatilize and remove the lead compound, and further, an alkali is introduced to remove the remaining chlorine.・ This is a method for reducing chlorine.

【0006】上記(1)(2)の鉛・塩素の低減方法におい
て、具体的には、塩素量は次式(II)に従って調整され
る。また、アルカリ添加量は次式(III)に従って調整さ
れる。 1< ([Cl]−[R])/[Pb] <15 …(II) ([Pb]は鉛化合物含有量の化学当量、[R]はアルカリ金
属化合物含有量の化学当量、[Cl]は塩素の化学当量) 1< ([R]+[R1])/[Cl] <3 …(III) ([R],[Cl]は上記に同じ、[R1]は添加するアルカリ金属
化合物の化学当量、さらに([R]+[R1])はクリンカー中の
2Oが0.75wt%以下となる量)
In the above methods (1) and (2) for reducing lead and chlorine, specifically, the amount of chlorine is adjusted according to the following formula (II). The amount of alkali added is adjusted according to the following formula (III). 1 <([Cl]-[R]) / [Pb] <15 (II) ([Pb] is the chemical equivalent of the lead compound content, [R] is the chemical equivalent of the alkali metal compound content, [Cl] Is the chemical equivalent of chlorine. 1 <([R] + [R1]) / [Cl] <3 (III) ([R] and [Cl] are the same as above, [R1] is the alkali metal compound to be added. Chemical equivalent, and ([R] + [R1]) is the amount of R 2 O in clinker that is 0.75 wt% or less)

【0007】さらに本発明は、セメント原料をキルンで
焼成してセメントクリンカーを製造する際に、原料中の
塩素量を鉛含有量に対する化学当量より過剰量に調整し
て焼成することにより鉛化合物を揮発除去し、さらにキ
ルンのクリンカー排出側またはキルンの途中からアルカ
リを導入してクリンカーに残留する塩素をアルカリ塩化
物に転じて除去する鉛・塩素の低減方法に関する。
Further, the present invention provides a method of producing a cement clinker by calcining a cement raw material in a kiln to adjust the amount of chlorine in the raw material to an excess of a chemical equivalent to the lead content and calcinate the lead compound. The present invention relates to a method for reducing lead and chlorine, which volatilizes and removes and further introduces an alkali from the clinker discharge side of the kiln or from the middle of the kiln to convert chlorine remaining in the clinker into an alkali chloride and remove it.

【0008】上記セメントクリンカー製造における鉛・
塩素の低減方法は、クリンカーを製造するロータリーキ
ルンにおいて、キルンの径(D)に対する長さ(L)が排出
端から4D〜12Dの範囲に、キルン内の原料に混入さ
れる全アルカリの50wt%以上を導入する方法を含む。
[0008] Lead in the production of the above cement clinker
In a rotary kiln for producing clinker, the length (L) with respect to the diameter (D) of the kiln is in the range of 4D to 12D from the discharge end, and 50% by weight or more of the total alkali mixed into the raw material in the kiln. Including a method to introduce.

【0009】また本発明は、上記セメントクリンカー製
造における鉛・塩素の低減方法に関連して、ロータリー
キルンのクリンカー排出端または中央部にアルカリ原料
の投入手段を設けたことを特徴とする鉛・塩素の低減装
置を提供する。
Further, the present invention relates to a method for reducing lead and chlorine in the production of cement clinker, wherein a means for introducing an alkali material is provided at a clinker discharge end or a central portion of the rotary kiln. A reduction device is provided.

【0010】[0010]

【発明の実施の態様】以下、本発明の鉛・塩素低減方法
を実施態様に基づいて詳細に説明する。本発明の方法
は、鉛化合物を含有する材料を塩素の存在下で塩化鉛の
沸点以上に加熱し、鉛化合物を塩化鉛に転じて揮発除去
する方法において、塩素量を鉛含有量に対する化学当量
より過剰量に調整して鉛化合物を揮発除去した後に、ア
ルカリを導入して残留する塩素をアルカリ塩化物に転じ
て加熱除去することを特徴とする鉛・塩素の低減方法で
ある。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The lead / chlorine reduction method of the present invention will be described below in detail based on embodiments. The method of the present invention is a method of heating a material containing a lead compound to a temperature higher than the boiling point of lead chloride in the presence of chlorine, and converting the lead compound to lead chloride to volatilize and remove the amount of chlorine relative to the lead content. This is a method for reducing lead / chlorine, which comprises adjusting the amount to an excessive amount, volatilizing and removing a lead compound, and then introducing an alkali to convert residual chlorine into an alkali chloride and removing it by heating.

【0011】本発明において、塩素量は原料の鉛含有量
に対してその化学当量よりやや過剰量となるように調整
される。具体的には、例えば、塩素の化学当量を[C
l]、鉛の化学当量を[Pb]とすると、反応系の塩素量
は鉛含有量に対して次式(I)の範囲に調整される。 1< [Cl]/[Pb] < 15 ・…(I)
In the present invention, the amount of chlorine is adjusted so as to be slightly larger than the chemical equivalent of the lead content of the raw material. Specifically, for example, the chemical equivalent of chlorine is [C
l], assuming that the chemical equivalent of lead is [Pb], the chlorine content of the reaction system is adjusted to the range of the following formula (I) with respect to the lead content. 1 <[Cl] / [Pb] <15 ... (I)

【0012】また、原料に鉛化合物と共にアルカリ金属
化合物が含有されている場合には、塩素量はこれらの合
計量に対する化学当量に対してやや過剰量に調整され
る。すなわち、アルカリ金属含有量の化学当量が[R]で
あるとき、塩素量は鉛含有量およびアルカリ含有量に対
して次式(II)の範囲に調整される。 1< ([Cl]−[R])/[Pb] <15 ・…(II)
When the raw material contains an alkali metal compound together with a lead compound, the amount of chlorine is adjusted to be a little excessive with respect to the chemical equivalent to the total amount of these. That is, when the chemical equivalent of the alkali metal content is [R], the chlorine content is adjusted to the range of the following formula (II) with respect to the lead content and the alkali content. 1 <([Cl] − [R]) / [Pb] <15... (II)

【0013】上記(I)式および(II)式において、この塩
素量が1より小さいと鉛化合物ないしアルカリ金属化合
物に対して塩素不足となり、鉛化合物およびアルカリ金
属の残留量が増す。一方、塩素量が15を超えると塩素
の残留量が多く、これを除去するために次の工程で多量
のアルカリが必要になる。後述する実施例に示すよう
に、この塩素量は、上記(I)式および(II)式において、
2以上〜10以下が好ましい。
In the above formulas (I) and (II), if the chlorine content is smaller than 1, the chlorine content of the lead compound or the alkali metal compound becomes insufficient, and the residual amounts of the lead compound and the alkali metal increase. On the other hand, when the chlorine amount exceeds 15, the residual amount of chlorine is large, and a large amount of alkali is required in the next step to remove the chlorine. As shown in Examples described later, the chlorine amount is determined by the above formulas (I) and (II).
Two or more and ten or less are preferable.

【0014】本発明の方法をセメントクリンカーの製造
に適用する場合、セメントクリンカーの原料に含まれる
塩素量およびアルカリ金属含有量に基づいて、塩素化反
応系の塩素量が上記(I)(II)式の範囲内になるように調
整する。具体的には、原料中の鉛化合物量やアルカリ含
有量に対して塩素量が少ない場合には塩化カルシウム等
の塩素源を補充する。一方、鉛化合物量やアルカリ含有
量に対して塩素量が上記(I)(II)式の範囲より大幅に過
剰であるときは炭酸ソーダ等のアルカリ源を添加する。
When the method of the present invention is applied to the production of cement clinker, the amount of chlorine in the chlorination reaction system is determined based on the amounts of chlorine and alkali metals contained in the raw material of cement clinker as described in (I) and (II) above. Adjust so that it is within the range of the formula. Specifically, when the amount of chlorine is smaller than the amount of lead compound or alkali in the raw material, a chlorine source such as calcium chloride is supplemented. On the other hand, when the amount of chlorine is significantly larger than the range of the above formulas (I) and (II) with respect to the amount of the lead compound and the alkali, an alkali source such as sodium carbonate is added.

【0015】次に、鉛化合物の塩素化と生成した塩化鉛
の揮発が進行した段階で、この反応系にアルカリ(炭酸
ナトリウム等のアルカリ金属源)を導入し、クリンカー
に残留する塩素を塩化ナトリウム等のアルカリ塩化物に
転じて除去する。このとき、アルカリを導入する時期が
早すぎると、鉛化合物の塩素化が妨げらるので好ましく
ない。
Next, at the stage where the chlorination of the lead compound and the volatilization of the generated lead chloride have progressed, an alkali (an alkali metal source such as sodium carbonate) is introduced into the reaction system, and chlorine remaining in the clinker is removed by sodium chloride. Turned into alkali chlorides and removed. At this time, if the timing of introducing the alkali is too early, it is not preferable because chlorination of the lead compound is hindered.

【0016】導入するアルカリ(アルカリ金属源)の量は
次のように定めればよい。すなわち上記(I)(II)式に従
って調整した塩素量からクリンカーに残留する塩素量を
算出し、この塩素量に対してアルカリ添加量を以下に示
す式(III)の範囲に定める。 1 < ([R]+[R1])/[Cl]< 3 (III) ここで、[R],[Cl]は上記に同じであり、[R1]は添加する
アルカリ化合物の化学当量である。また、通常のセメン
トでは、そのアルカリ含有量(R2O)は0.75wt%以下に
管理されているので、上記式(III)において、アルカリ
の合計量([R]+[R1])はクリンカー中のR2Oが0.75wt
%以下となる量に調整される。
The amount of the alkali (alkali metal source) to be introduced may be determined as follows. That is, the amount of chlorine remaining in the clinker is calculated from the amount of chlorine adjusted according to the above formulas (I) and (II), and the amount of alkali added is determined within the range of the following formula (III) with respect to this amount of chlorine. 1 <([R] + [R1]) / [Cl] <3 (III) Here, [R] and [Cl] are the same as above, and [R1] is the chemical equivalent of the alkali compound to be added. . Further, in ordinary cement, the alkali content (R 2 O) is controlled to 0.75 wt% or less, so that in the above formula (III), the total amount of alkali ([R] + [R1]) is 0.75wt of R 2 O in clinker
%.

【0017】なお、上記式(III)のアルカリ量は空気等
によって吹き込む場合、ガスによって系外に排出される
飛散率を考慮するのが好ましい。系外に排出されるアル
カリの飛散率は、アルカリ添加量に対し、ダストおよび
クリンカー中のアルカリ量を分析し、アルカリ添加量
[R1]に対するダスト中のアルカリ増加量[R2]の割合、
i.e. [R2]/[R1]×100 に基づいて求められる。また、
運転中は製造したクリンカーを蛍光X線で分析し、
[R]、[R1]、[Cl]、[Pb]を求め、この結果を次の
クリンカー製造にフィードバックして塩素量およびアル
カリ添加量を調整すると良い。
When the amount of alkali in the above formula (III) is blown by air or the like, it is preferable to consider the scattering rate of gas discharged outside the system. The scattering rate of the alkali discharged out of the system can be calculated by analyzing the amount of alkali in dust and clinker against the amount of alkali added.
Ratio of alkali increase [R2] in dust to [R1],
ie It is obtained based on [R2] / [R1] × 100. Also,
During operation, the produced clinker is analyzed by fluorescent X-ray,
[R], [R1], [Cl], and [Pb] are obtained, and the results are fed back to the next clinker production to adjust the chlorine amount and the alkali addition amount.

【0018】ロータリーキルンによるセメントクリンカ
ーの製造においては、キルンのアルカリ導入位置によっ
て上記反応系におけるアルカリ導入のタイミングを調整
することができる。具体的には、キルンの径(D)に対し
て長さ(L)がクリンカー排出端から4D〜12Dの範囲
に、キルン内の原料に混入される全アルカリの50wt%
以上を導入するのが好ましい。この長さ(L)が12Dよ
り大きい範囲(ie.キルンの入口に近い範囲)は塩素化反
応が初期段階の範囲であり、鉛化合物が十分に揮発して
いない。この範囲にアルカリが導入されると塩素がアル
カリによって消費されるので、鉛化合物の塩素化が抑制
され、鉛の残留量が多くなる。一方、アルカリ導入位置
の長さ(L)が4Dよりも小さいと、キルンの出口に近く
なり、導入したアルカリの反応時間が不足する。
In the production of cement clinker using a rotary kiln, the timing of alkali introduction in the above reaction system can be adjusted depending on the alkali introduction position of the kiln. Specifically, the length (L) is set within a range of 4D to 12D from the clinker discharge end with respect to the diameter (D) of the kiln, and 50 wt% of the total alkali mixed into the raw material in the kiln.
It is preferable to introduce the above. In the range where the length (L) is larger than 12D (ie, the range near the entrance of the kiln), the chlorination reaction is in the initial stage, and the lead compound is not sufficiently volatilized. When an alkali is introduced into this range, chlorine is consumed by the alkali, so that chlorination of the lead compound is suppressed and the residual amount of lead increases. On the other hand, if the length (L) of the alkali introduction position is smaller than 4D, it is close to the exit of the kiln, and the reaction time of the introduced alkali is insufficient.

【0019】キルンの上記範囲にアルカリを導入するた
めに、キルンのクリンカー排出端(出口)にアルカリの投
入手段を設けると良い。好ましくは、キルンの入口に、
原料投入手段、塩素源投入手段、およびアルカリ源投入
手段を設けて原料の塩素アルカリバランスを調整できる
ようにし、更に、キルンの排出端(出口)には残留塩素を
除去するためのアルカリ投入手段を設ける。この投入手
段として、例えば、アルカリを空気輸送する管路を設
け、そのキルン内の先端に吹き込みノズルを設けた構成
とすることができる。この吹き込み速度を調整すること
により、キルンの上記範囲にアルカリを導入することが
できる。また、キルンの途中に開閉蓋を設け、キルン1
回転毎に機械的にこの蓋を開けてアルカリを投入するな
どの手段により、キルン途中からアルカリを添加する方
法でもよい。
In order to introduce alkali into the above-mentioned range of the kiln, it is preferable to provide a means for introducing alkali at the clinker discharge end (outlet) of the kiln. Preferably, at the kiln entrance,
Raw material charging means, chlorine source charging means, and alkali source charging means are provided so that the chlor-alkali balance of the raw material can be adjusted.Furthermore, at the discharge end (outlet) of the kiln, an alkali charging means for removing residual chlorine is provided. Provide. As the charging means, for example, a configuration may be employed in which a pipeline for transporting the alkali by air is provided, and a blowing nozzle is provided at the tip in the kiln. By adjusting the blowing speed, alkali can be introduced into the above-mentioned range of the kiln. An opening / closing lid is provided in the middle of the kiln,
A method in which the alkali is added from the middle of the kiln by means such as opening the lid mechanically every rotation and introducing the alkali may be used.

【0020】本発明に係る好適な装置構成例を図1に示
す。図1の装置はセメントのクリンカー製造装置に本発
明を適用したものであり、ロータリーキルン6の入口側
に原料、塩素源およびアルカリ源を供給するホッパ1
3、14、15が各々設けられており、これらはコンベ
ア7を介してキルン6の入口に連接されている。また、
キルン入口には排ガスの冷却ダクト8が接続されてお
り、これにサイクロン9が介設されている。排ガス中の
揮発した塩類は冷却ダクト8を経由してサイクロン9に
導かれて分離濃縮され、その一部はキルンに回送され
る。サイクロン9にはバグフィルター10が接続してお
り、ここで捕集された鉛などのダストは精錬工程に送ら
れ回収される。排ガスはブロア11を経て系外に放出さ
れる。一方、キルン6の出口にはバーナ4および回収し
たクリンカーを冷却するクーラ5と共にアルカリ投入手
段1が設けられている。この投入手段1はアルカリを空
気搬送するブロア2と管路、および炉内の管路先端に設
けたノズル3を有し、ノズル先端の空塔速度が1〜15
m/sの流速でアルカリ源がノズル3から炉内に吹き込ま
れる。
FIG. 1 shows an example of a preferred apparatus configuration according to the present invention. The apparatus shown in FIG. 1 is an apparatus in which the present invention is applied to a clinker manufacturing apparatus for cement, and a hopper 1 for supplying a raw material, a chlorine source and an alkali source to an inlet side of a rotary kiln 6.
3, 14, and 15 are provided, and these are connected to an inlet of the kiln 6 via a conveyor 7. Also,
An exhaust gas cooling duct 8 is connected to the kiln inlet, and a cyclone 9 is interposed therebetween. The volatilized salts in the exhaust gas are led to a cyclone 9 via a cooling duct 8 to be separated and concentrated, and a part thereof is sent to a kiln. A bag filter 10 is connected to the cyclone 9, and dust such as lead collected here is sent to a refining process and collected. The exhaust gas is discharged outside the system via the blower 11. On the other hand, at the outlet of the kiln 6, an alkali injection means 1 is provided together with a burner 4 and a cooler 5 for cooling the recovered clinker. The charging means 1 has a blower 2 and a pipe for conveying the alkali by air, and a nozzle 3 provided at the tip of the pipe in the furnace.
An alkali source is blown into the furnace from the nozzle 3 at a flow rate of m / s.

【0021】[0021]

【発明の効果】本発明によれば、鉛の残留量と共に塩素
の残留量を大幅に低減することができる。具体的には、
クリンカ中のアルカリ量が0.75wt%を超えない範囲
で、クリンカ中の塩素量を1000ppm以下、好ましく
は数十ppmに低減することができる。さらに、クリンカ
中の鉛含有量を環境基準に適合する60ppm以下の水準
に低減することができる。このように、本発明によれば
廃棄物中の鉛含有量および塩素量を効果的に低減するこ
とができ、特に有害な鉛含有量を減少できるのでその安
全性が高まり、廃棄物処理を安全に行うことができる。
また鉛を回収する上でも有用である。さらに、都市ゴミ
焼却灰や下水汚泥焼却灰を本発明によって処理すればセ
メントにとって好ましくない鉛および塩素の残留量を格
段に低減できるので、これらをセメント原料として再利
用する場合に有利である。
According to the present invention, the residual amount of chlorine as well as the residual amount of lead can be greatly reduced. In particular,
As long as the alkali content in the clinker does not exceed 0.75 wt%, the chlorine content in the clinker can be reduced to 1000 ppm or less, preferably several tens ppm. Further, the lead content in the clinker can be reduced to a level of 60 ppm or less, which meets environmental standards. As described above, according to the present invention, the lead content and the chlorine content in the waste can be effectively reduced, and particularly, the harmful lead content can be reduced, so that the safety is enhanced, and the waste disposal can be performed safely. Can be done.
It is also useful for recovering lead. Furthermore, the treatment of municipal refuse incineration ash and sewage sludge incineration ash according to the present invention can significantly reduce the residual amounts of lead and chlorine that are undesirable for cement, which is advantageous when reusing these as cement raw materials.

【0022】[0022]

【実施例】以下、本発明を実施例によって具体的に示
す。
EXAMPLES The present invention will be specifically described below with reference to examples.

【0023】実施例1 セメント調合原料(Na2O:1.4wt%、K2O:0.8wt%、Cl:2.
7wt%、Pb:1800ppm、igloss:33wt%)1500kg/hに塩
化カルシウム7kg/hを添加して、図1に示すロータリー
キルンに投入し、1350℃の温度で90分焼成し、セ
メントクリンカー約1000kg/hを製造した。このクリ
ンカー中の塩素量・アルカリ量・鉛量を表1のNo.1に示
した。一方、上記原料1500kg/hに炭酸ソーダをおの
おの1kg/h,4kg/h,6kg/h添加して焼成した結果を表1
のNo.2〜No.4に示した。
Example 1 Raw materials for cement preparation (Na 2 O: 1.4 wt%, K 2 O: 0.8 wt%, Cl: 2.
7 wt%, Pb: 1800 ppm, igloss: 33 wt%) 1500 kg / h, 7 kg / h of calcium chloride was added, and the mixture was charged into a rotary kiln shown in FIG. h was manufactured. The amount of chlorine, alkali and lead in the clinker is shown in No. 1 of Table 1. On the other hand, the results obtained by adding sodium carbonate to the above-mentioned raw material 1500 kg / h and adding 1 kg / h, 4 kg / h, and 6 kg / h respectively and calcining are shown in Table 1.
No. 2 to No. 4 are shown.

【0024】No.1〜No.3の結果では、十分な量の塩素
の存在によりクリンカの鉛含有量は22ppmに低減して
いる。但し、残留塩素は0.23〜0.94wt%とやや高
く、これに伴いアルカリは殆ど残留せず、塩化アルカリ
となって揮発する。この塩化アルカリはバグフィルター
10によりダストとして回収される。一方、No.4に示
すように、アルカリに消費される量を差し引いた塩素量
([Cl]-[R])が鉛含有量に対して1.5当量になるとクリ
ンカに残留する鉛含有量はやや高くなる。なお、鉛含有
量に対する塩素量が1当量未満では塩素が全量反応して
も鉛が残留することになる。従って、鉛含有量に対する
塩素量{([Cl]-[R])/[Pb]}は1当量を超える量が必要で
あり、2当量以上が好ましい。これによりクリンカ中の
鉛含有量を数十ppmに低減することができる。
In the results of No. 1 to No. 3, the lead content of the clinker was reduced to 22 ppm due to the presence of a sufficient amount of chlorine. However, the residual chlorine is slightly high at 0.23 to 0.94 wt%, and almost no alkali remains, and the residual chlorine evaporates as alkali chloride. The alkali chloride is collected by the bag filter 10 as dust. On the other hand, as shown in No. 4, the amount of chlorine minus the amount consumed by alkali
When ([Cl]-[R]) becomes 1.5 equivalents to the lead content, the lead content remaining in the clinker becomes slightly higher. If the amount of chlorine relative to the lead content is less than 1 equivalent, lead will remain even if the entire amount of chlorine reacts. Therefore, the amount of chlorine {([Cl]-[R]) / [Pb]} relative to the lead content needs to be more than 1 equivalent, preferably 2 equivalents or more. Thereby, the lead content in the clinker can be reduced to several tens ppm.

【0025】次に、焼成前の原料系の塩素量を以上の範
囲に調整したものをロータリキルンに投入し、焼成時に
アルカリ(炭酸ソーダ)を添加した例(No.5〜No.7)につい
てみると、No.5の例では、鉛含有量に対する塩素量が
15当量を超えるために炭酸ソーダを50kg/h添加して
もクリンカの塩素残留量は0.16wt%とやや高い。一
方、No.6,No.7の例では、鉛含有量に対する塩素量が
2〜10当量の範囲であり、これに炭酸ソーダを25kg
/h、10kg/h(ie.1<{([R]+[R1])/[Cl]<3の範囲)
添加することにより、クリンカ中の鉛量、塩素量、アル
カリ量の何れも大幅に低減されている。この結果から、
鉛含有量に対する塩素量は15当量未満が適当であり、
2〜10当量が好ましい。また、焼成時に添加するアル
カリ量([R]+[R1])/[Cl])は1当量を超える量〜3当量未
満の量が好ましい。
Next, an example (No. 5 to No. 7) in which the amount of chlorine in the raw material system before the calcination was adjusted to the above range was charged into a rotary kiln, and an alkali (sodium carbonate) was added during the calcination. Looking at the example of No. 5, the chlorine content of the clinker is slightly high at 0.16 wt% even when 50 kg / h of sodium carbonate is added since the chlorine content with respect to the lead content exceeds 15 equivalents. On the other hand, in the examples of No. 6 and No. 7, the amount of chlorine relative to the lead content was in the range of 2 to 10 equivalents, and 25 kg of sodium carbonate was added thereto.
/ h, 10kg / h (in the range of ie.1 <{([R] + [R1]) / [Cl] <3)
By the addition, the amounts of lead, chlorine and alkali in the clinker are all greatly reduced. from this result,
The amount of chlorine relative to the lead content is suitably less than 15 equivalents,
2-10 equivalents are preferred. Further, the amount of alkali ([R] + [R1]) / [Cl]) added at the time of firing is preferably an amount exceeding 1 equivalent to less than 3 equivalents.

【0026】[0026]

【表1】 [Table 1]

【0027】実施例2 実施例1の試料No.1について、クリンカーに含まれる
鉛、アルカリおよび塩素の原料に対する各残留率をキル
ン内の焼成範囲ごとに調べた。この結果を図2に示し
た。なお、この焼成範囲はキルンの径(D)に対するバー
ナ側(出口側)からの長さ(L)によって示した。本例は原
料の成分調整および焼成時のアルカリ添加を行わない無
処理の焼成状態のものであるが、図示するように、キル
ン内がL/D=12以上の範囲(入口側の範囲)は塩素化の
初期段階であるので、塩素量と共に鉛含有量およびアル
カリ含有量が多いが、出口側に進むにつれて塩素化およ
び塩化物の揮発が進行した範囲となり、塩素量と共に鉛
含有量およびアルカリ含有量が減少し、概ねL/D=12
〜4の範囲では塩素は未だかなり残留しているが鉛とア
ルカリは大幅に減少し、L/D=4以下の範囲になると鉛
含有量は殆どゼロとなり、アルカリ量も40wt%以下の
水準にほぼ一定になる。従って、キルン内の概ねL/D=
12〜4の範囲にアルカリを添加することにより、残留
塩素との反応を進めてアルカリ塩化物を生成させること
により残留塩素量を低減することができる。
Example 2 With respect to the sample No. 1 of Example 1, the respective residual ratios of the lead, alkali and chlorine contained in the clinker to the raw materials were examined for each firing range in the kiln. The result is shown in FIG. The firing range was indicated by the length (L) from the burner side (outlet side) with respect to the kiln diameter (D). This example is a non-treated calcination state in which component adjustment of raw materials and alkali addition at the time of calcination are not performed, but as shown in the drawing, the inside of the kiln has a range of L / D = 12 or more (range on the inlet side). Since it is the initial stage of chlorination, the lead content and the alkali content are high together with the chlorine content, but the chlorination and the volatilization of the chloride proceed as the outlet side is reached, and the lead content and the alkali content increase with the chlorine content. The amount decreases, and L / D = 12
In the range of 44, chlorine still remains considerably, but lead and alkali are greatly reduced. When L / D = 4 or less, the lead content becomes almost zero, and the alkali content is reduced to a level of 40 wt% or less. It becomes almost constant. Therefore, L / D =
By adding an alkali in the range of 12 to 4, the reaction with residual chlorine is promoted to generate an alkali chloride, whereby the amount of residual chlorine can be reduced.

【図面の簡単な説明】[Brief description of the drawings]

【図1】 本発明に係る鉛・塩素低減手段を備えたキル
ンの概略図。
FIG. 1 is a schematic diagram of a kiln provided with a lead / chlorine reducing unit according to the present invention.

【図2】 キルン内の塩素、鉛およびアルカリの残留率
を示すグラフ。
FIG. 2 is a graph showing the residual ratio of chlorine, lead and alkali in a kiln.

フロントページの続き (72)発明者 田中 宣久 千葉県佐倉市大作二丁目4番2号 太平洋 セメント株式会社佐倉研究所内 (72)発明者 佐藤 宏一郎 千葉県佐倉市大作二丁目4番2号 太平洋 セメント株式会社佐倉研究所内 Fターム(参考) 4D004 AA36 AB03 AB06 BA02 BA05 CA30 CA34 CB09 CC11 CC12 DA02 DA03 DA06 DA10 Continued on the front page (72) Inventor Norihisa Tanaka 2-4-2 Daisaku, Sakura City, Chiba Pref. Inside the Sakura Research Laboratories, Pacific Cement Co., Ltd. (72) Inventor Koichiro Sato 2-4-2 Daisaku, Sakura City, Chiba Pref. Pacific Cement Stock 4D004 AA36 AB03 AB06 BA02 BA05 CA30 CA34 CB09 CC11 CC12 DA02 DA03 DA06 DA10

Claims (7)

【特許請求の範囲】[Claims] 【請求項1】 鉛化合物を含有する材料を、塩素の存在
下で塩化鉛の沸点以上に加熱し、鉛化合物を塩化鉛に転
じて揮発除去する方法において、塩素量を鉛含有量に対
して化学当量より過剰量に調整して鉛化合物を揮発除去
し、さらにアルカリを導入して残留する塩素をアルカリ
塩化物に転じて加熱除去することを特徴とする鉛・塩素
の低減方法。
1. A method of heating a material containing a lead compound to a temperature higher than the boiling point of lead chloride in the presence of chlorine to convert the lead compound into lead chloride and volatilize and remove the chlorine content relative to the lead content. A method for reducing lead and chlorine, comprising adjusting a chemical equivalent to an excess amount to volatilize and remove a lead compound, further introducing an alkali to convert residual chlorine into an alkali chloride, and removing by heating.
【請求項2】 塩素量を鉛化合物とアルカリの合計量に
対する化学当量より過剰量に調整して鉛化合物を揮発除
去し、さらにアルカリを導入して残留する塩素を除去す
る請求項1に記載する鉛・塩素の低減方法。
2. The method according to claim 1, wherein the amount of chlorine is adjusted to an excess of a chemical equivalent to the total amount of the lead compound and the alkali to volatilize and remove the lead compound, and further introduce an alkali to remove residual chlorine. How to reduce lead and chlorine.
【請求項3】 請求項2の方法において、塩素量を次式
(II)に従って調整する鉛・塩素の低減方法。 1< ([Cl]−[R])/[Pb] <15 …(II) ([Pb]は鉛化合物含有量の化学当量、[R]はアルカリ金
属化合物含有量の化学当量、[Cl]は塩素の化学当量)
3. The method of claim 2, wherein the amount of chlorine is
Lead and chlorine reduction method adjusted according to (II). 1 <([Cl]-[R]) / [Pb] <15 (II) ([Pb] is the chemical equivalent of the lead compound content, [R] is the chemical equivalent of the alkali metal compound content, [Cl] Is the chemical equivalent of chlorine)
【請求項4】 請求項1,2または3の方法において、
アルカリ添加量を次式(III)に従って調整する鉛・塩素の
低減方法。 1< ([R]+[R1])/[Cl] <3 …(III) ([R],[Cl]は上記に同じ、[R1]は添加するアルカリ金属
化合物の化学当量、さらに([R]+[R1])はクリンカー中の
2Oが0.75wt%以下となる量)
4. The method of claim 1, 2 or 3,
A method for reducing lead and chlorine in which the amount of alkali added is adjusted according to the following formula (III). 1 <([R] + [R1]) / [Cl] <3 (III) ([R] and [Cl] are the same as above, [R1] is the chemical equivalent of the alkali metal compound to be added, and ([ [R] + [R1]) is an amount such that R 2 O in the clinker becomes 0.75 wt% or less.)
【請求項5】 セメント原料をキルンで焼成してセメン
トクリンカーを製造する際に、原料中の塩素量を鉛含有
量に対する化学当量より過剰量に調整して焼成すること
により鉛化合物を揮発除去し、さらにキルンのクリンカ
ー排出側またはキルンの途中からアルカリを導入してク
リンカーに残留する塩素をアルカリ塩化物に転じて除去
する請求項1〜4のいずれかに記載する鉛・塩素の低減
方法。
5. When producing a cement clinker by calcining a cement raw material in a kiln, the amount of chlorine in the raw material is adjusted to an excess of a chemical equivalent to the lead content and calcined to volatilize and remove the lead compound. The method for reducing lead and chlorine according to any one of claims 1 to 4, wherein an alkali is introduced from the clinker discharge side of the kiln or from the middle of the kiln to remove chlorine remaining in the clinker into alkali chloride.
【請求項6】 クリンカーを製造するロータリーキルン
において、キルンの径(D)に対する長さ(L)が排出端か
ら4D〜12Dの範囲に、キルン内の原料に混入される
全アルカリの50wt%以上を導入する請求項5に記載す
る鉛・塩素の低減方法。
6. A rotary kiln for producing a clinker, wherein the length (L) with respect to the diameter (D) of the kiln is in the range of 4D to 12D from the discharge end, and 50% by weight or more of the total alkali mixed into the raw material in the kiln. The method for reducing lead and chlorine according to claim 5, which is introduced.
【請求項7】 ロータリーキルンのクリンカー排出端ま
たは中央部にアルカリ原料の投入手段を設けたことを特
徴とする鉛・塩素の低減装置。
7. An apparatus for reducing lead and chlorine, comprising means for introducing an alkaline material at a clinker discharge end or a central portion of a rotary kiln.
JP23388599A 1999-08-20 1999-08-20 Lead and chlorine reduction method and apparatus Expired - Lifetime JP4283947B2 (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005320218A (en) * 2004-05-11 2005-11-17 Taiheiyo Cement Corp Manufacturing method of cement feed material
JP2006314987A (en) * 2005-04-14 2006-11-24 Taiheiyo Cement Corp Method for treating chlorine-containing dust
US7265254B2 (en) * 2001-07-30 2007-09-04 Taiheiyo Cement Corporation Waste processing method, waste processing system, integrated waste processing method, and integrated waste processing system
JP2007246352A (en) * 2006-03-17 2007-09-27 Taiheiyo Cement Corp Method for removing and recovering heavy metal from cement production stage
JP2008137826A (en) * 2006-11-30 2008-06-19 Taiheiyo Cement Corp Cement clinker, cement using the same and solidifying material

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7265254B2 (en) * 2001-07-30 2007-09-04 Taiheiyo Cement Corporation Waste processing method, waste processing system, integrated waste processing method, and integrated waste processing system
JP2005320218A (en) * 2004-05-11 2005-11-17 Taiheiyo Cement Corp Manufacturing method of cement feed material
JP2006314987A (en) * 2005-04-14 2006-11-24 Taiheiyo Cement Corp Method for treating chlorine-containing dust
JP4566134B2 (en) * 2005-04-14 2010-10-20 太平洋セメント株式会社 Treatment method for chlorine-containing dust
JP2007246352A (en) * 2006-03-17 2007-09-27 Taiheiyo Cement Corp Method for removing and recovering heavy metal from cement production stage
JP4579178B2 (en) * 2006-03-17 2010-11-10 太平洋セメント株式会社 Methods for removing and recovering heavy metals from the cement manufacturing process
JP2008137826A (en) * 2006-11-30 2008-06-19 Taiheiyo Cement Corp Cement clinker, cement using the same and solidifying material

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